To assess the impact of phthalates on soil microorganisms and to supplement
the environmental risk assessment for these xenobiotics, soil was treated
with diethyl phthalate (DEP) or di (2-ethyl hexyl) phthalate (DEHP) at 0.1
to 100 mg/g. Bioavailability and membrane disruption were proposed as the c
haracteristics responsible for the observed fate and toxicity of both compo
unds. Diethyl phthalate was biodegraded rapidly in soil with a half-life (t
(50)deg) of 0.75 d at 20 degrees C, and was not expected to persist in the
environment. The DEHP, although biodegradable in aqueous solution (t(50)deg
< 15 d at 20 degrees C), was recalcitrant in soil, because of poor bioavai
lability (only 10% degraded by 70 d at 20 degrees C) and was predicted to a
ccount for the majority of phthalate contamination in the environment. Addi
tion of DEP or DEHP to soil at a concentration similar to that detected in
nonindustrial environments (0.1 mg/g) had no impact on the structural diver
sity (bacterial numbers, fatty acid methyl ester analysis) or functional di
versity (BIOLOG) of the microbial community. At concentrations representati
ve of a phthalate spill, DEP (>1 mg/g) reduced numbers of both total cultur
able bacteria (by 47%) and pseudomonads (by 62%) within 1 d. This was due t
o disruption of membrane fluidity by the lipophilic phthalate, a mechanism
not previously attributed to phthalates. However, DEHP had no effect on the
microbial community or membrane fluidity, even at 100 mg/g, and was predic
ted to have no impact on microbial communities in the environment.